Location: Range and Meadow Forage Management Research
2024 Annual Report
Objectives
The long-term objective of this project is to develop practices and strategies to restore and conserve Great Basin rangelands. Specifically, during the next five years we will focus on the following objectives:
Objective 1 (Restoration): Develop practices and strategies for restoring perennial livestock forages and ecosystem function on degraded and fire-prone Great Basin rangelands using combinations of grazing management, vegetation treatments, seed enhancements, and traditional restoration techniques.
Subobjective 1A: Develop seed enhancement technologies for overcoming barriers to rangeland seeding success. (Davies, Boyd, Copeland)
Subobjective 1B: Determine appropriate seed mixes for use after wildfires to limit exotic annual grass invasion and restore productivity. (Davies, Boyd, Copeland)
Subobjective 1C: Develop and evaluate management practices for controlling juniper encroachment of sagebrush steppe plant communities. (Bates, Davies)
Subobjective 1D: Determine post-treatment change in vegetation composition and structure over a 30 year time horizon in cut compared with burned juniper-encroached sagebrush steppe. (Boyd, Bates, Davies)
Objective 2 (Conservation): Develop practices and strategies (including decision-support tools) to maintain and enhance livestock forage production and other ecosystem services in rangelands across different site characteristics, climate conditions, and management systems.
Subobjective 2A: Evaluate grazing management as a tool to decrease wildfire risk, behavior, and severity. (Davies, Bates, Boyd, Copeland)
Subobjective 2B: Evaluate post-fire grazing management effects on herbaceous productivity and sage-grouse habitat. (Bates, Davies)
Subobjective 2C: Determine the influence of site attributes and climate variation on long-term productivity and diversity of sagebrush steppe. (Bates, Davies, Copeland)
Subobjective 2D: Develop a science-based framework for management planning. (Boyd, Bates, Davies)
Subobjective 2E: Use precision management technologies (global positioning of livestock, virtual fencing, remote sensing of landscape and others) to enhance livestock producer capability for optimum management of pastures and rangelands, balancing production and ecosystem services.
Approach
Objective 1: Hypotheses: 1) Incorporating seeds into activated carbon pellets will protect seeded vegetation from pre-emergent herbicides, 2) Seeds treated with abscisic acid will have delayed germination and increased seedling density relative to non-coated seeds, 3) Coating and imbibing treatments will produce similar seedling densities, 4) The effects of abscisic acid treatment will be dependent on level of coating; based on previous lab work we hypothesize that intermediate levels of treatment will produce highest seedling densities, 5) Drill seeding a mixture of native and introduced bunchgrasses after wildfire in sagebrush steppe will reduce exotic annual grass invasion compared to seeding native bunchgrasses, seeding introduced bunchgrasses, and not seeding, 6) Burning juniper-encroached sagebrush steppe will increase desirable herbaceous production, 7) Herbaceous vegetation productivity and abundance will be greater when juniper is controlled with either fall broadcast burning treatment or clear-cut/slash burning treatment compared to untreated woodlands, 8) Clear-cut/slash burning of encroaching junipers will produce more favorable habitat characteristics for sage-grouse compared to fall broadcast burning, 9) Juniper cover and density will increase at a faster rate in cut vs. burned western juniper plant communities, 10) Cover and density of mountain big sagebrush will decrease in association with burning but will recover to levels in cut treatments within 30 years, 11) Rate of increase in density and cover of large perennial bunchgrasses will be faster in burned vs. cut treatments, and 12) exotic annual grasses will initially increase more in the burned compared to the cut treatment.
Objective 2:Hypotheses: 1) moderate livestock grazing compared to grazing exclusion will reduce fine fuel continuity, height, total biomass, and accumulation of residual biomass on perennial grass crowns and 2) decrease fire-induced mortality of perennial grasses and thereby reduce post-fire exotic annual grass invasion, 3) increasing grazing pressure will reduce fuels and thereby decrease fire ignition potential and propagation, 4) Long-term heavy rotational grazing after fire will decrease herbaceous productivity, sage-grouse dietary forbs, and horizontal screening cover compared to light, moderate, and no grazing treatments, and 5) No grazing and light grazing will have greater herbaceous productivity, sage-grouse dietary forbs, and horizontal screening cover than moderate grazing.
Experimental approaches and research procedures: We will use a combination of grow room studies and small and large replicated field studies to answer these research questions. Many of these field studies will be long-term studies. If initial research plan is unsuccessful, we will revise our grow room and field studies to address the reasons why our initial research plan was unsuccessful or replicate the original experiment if it was unsuccessful because of an act of nature.
Progress Report
This is the final project report for 2070-21630-003-000D. The newly certified project, 2070-21500-001-000D, will build upon and expand this research.
In support of Objective 1, ARS scientists in Burns, Oregon, collected data on grow room and field experiments designed to test the effectiveness of activated seed coatings and carbon pellets at protecting seeds from pre-emergent herbicide damage. ARS researchers in Burns, Oregon, prepared peer-reviewed manuscripts on the effects of activated carbon pellets on protecting seeded species from pre-emergent herbicides. ARS researchers in Burns, Oregon, also collected data on grow room and field plots designed to evaluate coating and imbibing seeds with abscisic acid to delay germination. They also prepared a peer-reviewed manuscript on seed enhancement technologies. As well, the researchers and support staff collected data on experiments evaluating drill seeding native compared to non-native grasses after wildfire and experiments investigating the effects of burning juniper on herbaceous production. Researchers in Burns, Oregon, prepared peer-reviewed manuscripts on the effects of seeding native bunchgrasses, introduced bunchgrasses, or introduced and native bunchgrasses together after wildfire in sagebrush steppe communities.
In support of Objective 2, ARS researchers in Burns, Oregon, continued to collect data on experiments designed to evaluate grazing management as a tool to decrease wildfire probability, behavior, and severity. They also prepared peer-reviewed manuscripts on the effects of pre-fire grazing on post-fire community recovery. As well, ARS researchers continue to evaluate the effects of grazing after fire in sagebrush steppe communities. They also prepared peer-reviewed manuscripts on the effects of grazing after fire in annual grass invaded sagebrush steppe communities and non-invaded plant communities. ARS researchers in Burns, Oregon, continue to develop management-oriented materials to guide rangeland management based on ecological threats and the influence of management and non-management factors on plant community change.
Accomplishments
1. Using virtual fencing to create fuel breaks in the sagebrush steppe. Fuel breaks can be effective in combating wildfires in the Western United States; however, fine fuels must be maintained within acceptable abundance levels for maximum efficacy. Livestock grazing is a logical and potentially effective tool for maintaining fine fuels within acceptable levels of abundance. However, most fuel breaks are not fenced and fencing or herding cost may preclude the use of livestock grazing in targeted fine fuels management. The effectiveness of virtual fencing for spatially targeting cattle grazing within the bounds of a pasture-scale fuel break in the sagebrush steppe was tested. ARS researchers in Burns, Oregon, found that virtual fencing was highly effective in containing cattle locations and associated forage utilization within fuel break boundaries for dry cows, but less effective for cows with calves. Virtual fencing, particularly when combined with geospatial technologies for mapping grass fuel accumulations, has strong potential for use in managing grass fuel abundance within fuel breaks and potentially larger rangeland landscapes to benefit a wide variety of management expectations and values.
Review Publications
Smith, M.D., Wilkins, K.D., Holdrege, M.C., Wilfahrt, P., Collins, S.L., Knapp, A.K., Sala, O.E., Dukes, J.S., Phillips, R.P., Yahdjian, L., Gherardi, L.A., Ohlert, T., Beier, C., Fraser, L.H., Jentsch, A., Loik, M.E., Maestre, F.T., Power, S.A., Yu, Q., Felton, A.J., Larson, J.J., O'Connor, R.C., Zuo, X., et al. 2024. Extreme drought impacts have been underestimated in grasslands and shrublands globally. Proceedings of the National Academy of Sciences (PNAS). 121(4). Article e2309881120. https://doi.org/10.1073/pnas.2309881120.
Copeland, S.M., Davies, K.W., Boyd, C.S. 2024. Sagebrush ecosystems are more than Artemisia: The complex issue of degraded understories in the Great Basin. Rangeland Ecology and Management. 94:184-194. https://doi.org/10.1016/j.rama.2024.03.007.
Holfus, C.M., Boyd, C.S., Rios, R.C., Davies, K.W., Copeland, S.M., Mata-Gonzalez, R. 2023. Wyoming big sagebrush transplant survival and growth affected by age, season of planting, and competition. Rangeland Ecology and Management. 92:1-11. https://doi.org/10.1016/j.rama.2023.09.005.
Funk, J.L., Larson, J.J., Blair, M.D., Nguyen, M.A., Rivera, B.J. 2024. Drought response in herbaceous plants: A test of the integrated framework of plant form and function. Functional Ecology. 38(3):679-691. https://doi.org/10.1111/1365-2435.14495.
Bates, J.D., Davies, K.W. 2023. Grazing intensity effects on herbaceous community composition in burned sagebrush-steppe. Ecosphere. 14(10). Article e4671. https://doi.org/10.1002/ecs2.4671.
O'Connor, R.C., Fox, V.G., Hamerlynck, E.P. 2024. Photosynthetic resilience of Elymus elymoides and Pseudoroegneria spicata seedlings following acute water stress. Rangeland Ecology and Management. 94:195-198. https://doi.org/10.1016/j.rama.2024.03.012.
Davies, K.W., Boyd, C.S., Svejcar, L.N., Clenet, D.R. 2023. Long-term effects of revegetation efforts in annual grass-invaded rangeland. Rangeland Ecology and Management. 92:59-67. https://doi.org/10.1016/j.rama.2023.10.001.
Winkler, D.E., Garbowski, M., Kozic, K., Ladouceur, E., Larson, J.J., Martin, S., Rosche, C., Roscher, C., Slate, M.L., Korell, L. 2024. Facilitating comparable research in seedling functional ecology. Methods in Ecology and Evolution. 15(3):464-476. https://doi.org/10.1111/2041-210X.14288.
Ehlert, K., Brennan, J., Beard, J., Reuter, R., Menendez, H., Vandermark, L., Stephenson, M., Hoag, D., Meiman, P., O'Connor, R.C., Noelle, S. 2024. What’s in a name? Standardizing terminology for the enhancement of research, extension, and industry applications of virtual fence use on grazing livestock. Rangeland Ecology and Management. 94:199-206. https://doi.org/10.1016/j.rama.2024.03.004.
Olsoy, P.J., Zaiats, A., Delparte, D.M., Germino, M.J., Richardson, B.A., Roser, A.V., Forbey, J.S., Cattau, M.E., Caughlin, T.T. 2024. Demography with drones: Detecting growth and survival of shrubs with unoccupied aerial systems. Restoration Ecology. 32(4). Article e14106. https://doi.org/10.1111/rec.14106.
Davies, K.W., Schroeder, V.M., Johnson, D.D., Svejcar, L.N., Clenet, D.R. 2024. Spring-applied treatments offer another window of opportunity for revegetation of annual grass-invaded rangelands. Rangeland Ecology and Management. 93:104-111. https://doi.org/10.1016/j.rama.2024.01.002.
Olsoy, P.J., Sorenson, K.J. 2024. First record of Tricolored Blackbirds in Idaho. Western Birds. 55(1):43-50. https://doi.org/10.21199/WB55.1.3.
Bertuol-Garcia, D., Ladouceur, E., Brudvig, L.A., Laughlin, D.C., Munson, S.M., Curran, M.F., Davies, K.W., Svejcar, L.N., Shackelford, N. 2023. Testing the hierarchy of predictability in grassland restoration across a gradient of environmental severity. Ecological Applications. 33(8). Article e2922. https://doi.org/10.1002/eap.2922.
Fernández-Pascual, E., Carta, A., Rosbakh, S., Guja, L., Phartyal, S.S., Silveira, F.A., Chen, S., Larson, J.J., Jiménez-Alfaro, B. 2023. SeedArc, a global archive of primary seed germination data. New Phytologist. 240(2):466-470. https://doi.org/10.1111/nph.19143.
Copeland, S.M. 2024. Weak effects of a soil contrast on Wyoming big sagebrush (Artemisia tridentata ssp. wyomingensis) transplant survival in a northern Great Basin case study suggest importance of microsite selection and non-soil factors. Rangelands. 46(3):88-97. https://doi.org/10.1016/j.rala.2023.12.003.
Svejcar, L.N., Davies, K.W., Ritchie, A.L. 2023. Ecological restoration in the age of apocalypse. Global Change Biology. 29(17):4706-4710. https://doi.org/10.1111/gcb.16809.
Beck, J.L., Christiansen, T.J., Davies, K.W., Dinkins, J.B., Monroe, A.P., Naugle, D.E., Schroeder, M.A. 2023. Sage-grouse. In: McNew, L.B., Dahlgren, D.K., Beck, J.L., editors. Rangeland Wildlife Ecology and Conservation. New York, NY: Springer, Cham. p. 295-338. https://link.springer.com/chapter/10.1007/978-3-031-34037-6_10.
Davies, K.W., Bates, J.D., Boyd, C.S. 2023. Is crested wheatgrass invasive in sagebrush steppe with intact understories in the Great Basin? Rangeland Ecology and Management. 90:322-328. https://doi.org/10.1016/j.rama.2023.03.004.
Copeland, S.M., Condon, L., Rosentreter, R., Miller, J., Kahn-Abrams, M. 2023. Biocrusts indicators of livestock grazing effects on soil stability in sagebrush steppe: A case study from a long-term experiment in the northern Great Basin. Rangeland Ecology and Management. 91:82-86. https://doi.org/10.1016/j.rama.2023.09.001.
Davies, K.W., Copeland, S.M., Clenet, D.R., Svejcar, L.N., Bates, J.D. 2023. Influence of directional side of sagebrush canopies and interspaces on microhabitats. Basic and Applied Ecology. 72:16-21. https://doi.org/10.1016/j.baae.2023.06.004.
Smith, J.T., Allred, B.W., Boyd, C.S., Davies, K.W., Kleinhesselink, A.R., Morford, S.L., Naugle, D.E. 2023. Fire needs annual grasses more than annual grasses need fire. Biological Conservation. 286. Article 110299. https://doi.org/10.1016/j.biocon.2023.110299.
Davies, K.W., Bates, J.D., Svejcar, L.N. 2022. Reducing exotic annual grass competition did not improve shrub restoration success during a drought. Rangeland Ecology and Management. 85:9-14. https://doi.org/10.1016/j.rama.2022.08.001.
Svejcar, L.N., Kerby, J.D., Svejcar, T.J., Mackey, B.E., Boyd, C.S., Baughman, O.W., Madsen, M.D., Davies, K.W. 2022. Plant recruitment in drylands varies by site, year, and seeding technique. Restoration Ecology. 31(2). Article e13750. https://doi.org/10.1111/rec.13750.
Bates, J.D., Johnson, D., Davies, K.W., Svejcar, T., Hardegree, S.P. 2023. Effects of annual weather variation on peak herbaceous yield date in sagebrush steppe. Western North American Naturalist. 83(2):220-231. https://doi.org/10.3398/064.083.0207.
Pyke, D.A., Boyd, C.S. 2023. Manipulation of rangeland wildlife habitat. Book Chapter. p. 107-146. https://doi.org/10.1007/978-3-031-34037-6_5.
Miller, J.E., Copeland, S.M., Davies, K., Anacker, B., Safford, H., Harrison, S. 2022. Plant community data from a statewide survey of paired serpentine and non-serpentine soils in California, USA. Ecology. 103(6). Article e3644. https://doi.org/10.1002/ecy.3644.